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1995-03-22_GENERAL DOCUMENTS - M1977451 (4)
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1995-03-22_GENERAL DOCUMENTS - M1977451 (4)
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Last modified
4/14/2022 10:01:52 AM
Creation date
11/23/2007 6:58:06 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1977451
IBM Index Class Name
General Documents
Doc Date
3/22/1995
Doc Name
IKE 1 MINE PN M-77-451
From
COTTER CORP
To
DMG
Media Type
D
Archive
No
Tags
DRMS Re-OCR
Description:
Signifies Re-OCR Process Performed
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SR-I I (Ike #1 Mine) Designated Mining Operation <br /> January 31, 1995 - Page 4 <br /> The other important factor in solubility is the pH of the solution. <br /> As can be seen on the accompanying Eh-pH diagram for the U-OZ-HZO-CO2 <br /> system, "uranyl carbonate complexing causes a wide field of <br /> solubility to exist under conditions at all pH values" (Hostetler <br /> and Garrels, 1962 , p. 143) at low temperatures in both oxidizing and <br /> mildly reducing waters. Therefore, it appears that weathering of <br /> a uranium mine waste dump could produce a toxic uranium leachate. <br /> However, as Gableman put it, "the geologic problem for uranyl ions <br /> is not their mobility but their fixation in the low-temperature <br /> surficial environments" (Gableman, 1977, page 19) . <br /> It is a well established fact that uranium can be fixed by <br /> reduction of U+6 back to U+4. This is often done by organic <br /> compounds on which U+6 will absorb and later be reduced. This <br /> happens easier in acidic solutions than basic solutions. Other <br /> ways in which uranium is fixed, even without being reduced, are by <br /> absorption into clays and, at least temporarily, on fresh iron <br /> hydroxides. Even in the oxidizing environment, the uranyl ion, <br /> UOz+Z, will form many secondary minerals. In dry environments <br /> uranyl silicates, carbonates, and sulfates form by evaporation and <br /> are fairly stable at the surface as hydrated forms with Na, Mg, and <br /> Ca. Furthermore, U+6 will precipitate easily as phosphates, <br /> arsenates, and vanadates. The latter minerals are of the utmost <br /> importance in considering weathering of Salt Wash ores. Therefore, <br /> the geochemistry of vanadium will be discussed next. <br /> Vanadium generally occurs in nature in three valence states: V+3, <br /> the reduced state forms oxide minerals; V+4, in alumino-silicate <br /> minerals; and the V+5 oxidized state in the weathering cycle and in <br /> sedimentary rocks. Like uranium, during weathering vanadium is <br /> oxidized to soluble ions which are able to travel in solution over <br /> a wide range of acidity or alkalinity. Similarly, the presence of <br /> other components in an aqueous system controls the solubility of <br /> vanadium. Uranium oxidized to U+6 easier that vanadium does to V+5 <br /> all other conditions being the same. Although vanadium oxidizes <br /> similar to uranium, there are no known complexes between uranyl <br /> ions and vanadium to transport uranium, as there are with <br /> phosphates. <br /> Precipitation or fixation of vanadium can be brought about by <br /> several processes, including: 1) reducing agents such as organics <br /> or H2S, 2) presence of divalent cations of Pb, Zn, Cu which form <br /> insoluble compounds 3) by hydroxides of Al or ferric iron, and 4) <br /> precipitation of vanadates in the presence of divalent uranyl <br /> cations, (UO2) +2 . Even though vanadium is not scavenged by Fe and <br /> Mn oxides, as many other metals are in the secondary environment, <br /> it is generally concentrated in the ferruginous zone of soils in <br /> the V+5 state while V+3 will concentrate in the clay fraction. <br /> Although uranium and vanadium are each fairly soluble under similar <br /> oxidizing, either slightly acid or slightly alkaline conditions, <br /> together in the same natural solution, they will precipitate as the <br />
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